| Literature DB >> 35631718 |
Anna Scoppola1, Simone Cardoni1, Thomas Marcussen2, Marco Cosimo Simeone1.
Abstract
Viola sect. Melanium, the so-called pansy, is an allopolyploid morphologically well-defined lineage of ca. 110 perennial and annual species in the northern hemisphere, characterized by markedly complex genomic configurations. Five annual pansies occur in Italy, four of which are morphologically very similar and belong to the informal 'V. tricolor species complex': V. arvensis (2n = 34), V. hymettia (2n = 16), V. kitaibeliana (2n = 16), and V. tricolor (2n = 26). Their field recognition is difficult and reflects a long-debated taxonomy often resulting in doubtful records in field inventories and across European herbaria. The current lack of comprehensive intra- and interspecific comparative studies and a relative scarcity of appropriate genetic markers coupled with unambiguous cytological descriptions are hindering clear taxa circumscription and phylogenetic inferences within this group. In this work, we tested DNA sequence variation of three highly variable plastid markers and High-Throughput Sequencing (HTS) of the nuclear ribosomal 5S-IGS region in an attempt to decipher species identity within the V. tricolor species complex and to obtain an insight on their genome organization and evolution. Our results document the close relationships within this species group, a reliable molecular resolution for V. tricolor, and the common ancestry of V. arvensis and the poorly differentiated V. kitaibeliana and V. hymettia. Evidence of an important inter-population geographical divergence was recorded in V. tricolor and V. arvensis, pointing at the existence of different eco-cytotypes within these entities. Overall diversity patterns and the occurrence of two to four differently diverging 5S-IGS lineages are discussed in the light of the acknowledged taxonomy and genomic evolutive trajectories of sect. Melanium.Entities:
Keywords: 5S-IGS nuclear DNA; Melanium; Viola; evolution; high-throughput-sequencing; plastid DNA
Year: 2022 PMID: 35631718 PMCID: PMC9147628 DOI: 10.3390/plants11101294
Source DB: PubMed Journal: Plants (Basel) ISSN: 2223-7747
Estimates of mean evolutionary divergence over sequence pairs within and between taxa for the three combined plastid markers.
| Taxon | N | Intra- | Inter-Group | H_tot | H_sh | Hd | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
| 21 | 0.004 | 0.001 | 0.001 | 0.001 | 0.001 | 0.002 | 0.005 | 0.002 | 0.002 | 0.001 | 12 | 4 | 0.904 | |
| 1 | - | 0.005 | 0.002 | 0.002 | 0.001 | 0.002 | 0.005 | 0.001 | 0.002 | 0.001 | 1 | - | - | ||
|
| 8 | 0.001 | 0.003 | 0.006 | 0 | 0.002 | 0.002 | 0.005 | 0.002 | 0.002 | 0.002 | 6 | 2 | 0.893 | |
|
| 7 | 0.001 | 0.003 | 0.006 | 0.001 | 0.002 | 0.002 | 0.005 | 0.002 | 0.002 | 0.002 | 5 | 3 | 0.857 | |
|
| 16 | 0.002 | 0.005 | 0.004 | 0.007 | 0.007 | 0.002 | 0.005 | 0.002 | 0.002 | 0.001 | 8 | 1 | 0.7 | |
|
| 1 | - | 0.007 | 0.005 | 0.008 | 0.007 | 0.006 | 0.005 | 0.002 | 0.002 | 0.002 | 1 | - | - | |
|
| 1 | - | 0.048 | 0.045 | 0.047 | 0.047 | 0.05 | 0.049 | 0.005 | 0.005 | 0.005 | 1 | - | - | |
|
| 1 | - | 0.006 | 0.003 | 0.006 | 0.006 | 0.005 | 0.006 | 0.048 | 0.002 | 0.001 | 1 | - | - | |
|
| 1 | - | 0.009 | 0.006 | 0.01 | 0.009 | 0.007 | 0.007 | 0.05 | 0.006 | 0.002 | 1 | - | - | |
|
| 1 | - | 0.004 | 0.001 | 0.005 | 0.005 | 0.003 | 0.005 | 0.046 | 0.001 | 0.006 | 1 | - | - | |
Standard error estimates are shown above the diagonal; color graduation—minimum (crimson) to maximum (dark green) values. N—Number of sequences; H_tot—total haplotypes found in each taxon; H_sh—number of shared haplotypes; Hd—haplotype diversity.
Figure 1Median Joining haplotype network of the trnH-psbA + rps19-trnH + trnD-trnY concatenated regions in the investigated dataset. Colors identify the different species and the ecological features of each sample are reported (detailed in Supplementary File S1). Line shape and thickness indicate the relative number of mutations separating each haplotype. L1–L3 = inferred haplotype lineages.
Estimates of mean evolutionary divergence over sequence pairs for the nuclear 5S-HTS sequences with abundance ≥5.
| Sample | d | S.E. | Sample | d | S.E. | Sample | d | S.E. | Sample | d | S.E. | |
|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
| T14 | 0.060 | 0.010 | - | - | - | - | - | - | - | - | - |
|
| T16 | 0.100 | 0.010 | - | - | - | - | - | - | - | - | - |
|
| T17 | 0.060 | 0.010 | T18 | 0.070 | 0.010 | T20 | 0.070 | 0.010 | - | - | - |
|
| T2 | 0.120 | 0.010 | T6 | 0.120 | 0.010 | T8 | 0.110 | 0.010 | T9 | 0.140 | 0.010 |
|
| T24 | 0.070 | 0.010 | T26 | 0.060 | 0.010 | T28 | 0.060 | 0.010 | - | - | - |
|
| T29 | 0.130 | 0.010 | - | - | - | - | - | - | - | - | - |
|
| T30 | 0.130 | 0.010 | - | - | - | - | - | - | - | - | - |
color graduation: minimum (crimson) to maximum (dark green) values.
Intragenomic mean divergence.
| Intra- | Inter-Species | ||||||||
|---|---|---|---|---|---|---|---|---|---|
| N |
|
|
|
|
|
| |||
| 1 | - | ||||||||
|
| 7 | 0.071 | 0.117 | ||||||
|
| 1 | - | 0.114 | 0.118 | |||||
|
| 1 | - | 0.123 | 0.118 | 0.124 | ||||
|
| 8 | 0.067 | 0.12 | 0.073 | 0.119 | 0.119 | |||
|
| 5 | 0.071 | 0.119 | 0.073 | 0.118 | 0.118 | 0.07 | ||
|
| 4 | 0.118 | 0.122 | 0.11 | 0.124 | 0.128 | 0.11 | 0.111 | |
d—distance; S.E.—Standard error. (b) intra- and interspecific mean divergence; N—number of individuals; color graduation: minimum (crimson) to maximum (dark green) values.
Mean divergence among the ‘V. tricolor species complex’ samples.
| N | T10 | T12 | T14 | T17 | T18 | T2 | T20 | T21 | T24 | T25 | T26 | T27 | T28 | T6 | T8 | T9 | |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 4 | |||||||||||||||||
| 2 | 0.075 | ||||||||||||||||
| 1 | 0.073 | 0.065 | |||||||||||||||
| 1 | 0.068 | 0.066 | 0.063 | ||||||||||||||
| 1 | 0.075 | 0.072 | 0.070 | 0.064 | |||||||||||||
| 1 | 0.109 | 0.111 | 0.111 | 0.107 | 0.113 | ||||||||||||
| 1 | 0.080 | 0.074 | 0.073 | 0.067 | 0.073 | 0.111 | |||||||||||
| 2 | 0.078 | 0.072 | 0.072 | 0.069 | 0.073 | 0.112 | 0.076 | ||||||||||
| 1 | 0.072 | 0.069 | 0.067 | 0.059 | 0.067 | 0.108 | 0.069 | 0.071 | |||||||||
| 2 | 0.066 | 0.067 | 0.063 | 0.055 | 0.064 | 0.108 | 0.069 | 0.069 | 0.059 | ||||||||
| 1 | 0.074 | 0.072 | 0.069 | 0.061 | 0.070 | 0.108 | 0.070 | 0.075 | 0.064 | 0.060 | |||||||
| 3 | 0.067 | 0.068 | 0.065 | 0.058 | 0.065 | 0.108 | 0.070 | 0.069 | 0.061 | 0.055 | 0.062 | ||||||
| 1 | 0.081 | 0.074 | 0.074 | 0.069 | 0.074 | 0.112 | 0.073 | 0.075 | 0.071 | 0.071 | 0.073 | 0.071 | |||||
| 1 | 0.105 | 0.107 | 0.107 | 0.105 | 0.110 | 0.111 | 0.111 | 0.108 | 0.106 | 0.106 | 0.109 | 0.107 | 0.111 | ||||
| 1 | 0.098 | 0.096 | 0.096 | 0.094 | 0.098 | 0.110 | 0.098 | 0.097 | 0.095 | 0.096 | 0.098 | 0.096 | 0.098 | 0.105 | |||
| 1 | 0.116 | 0.112 | 0.114 | 0.111 | 0.115 | 0.125 | 0.113 | 0.112 | 0.112 | 0.115 | 0.116 | 0.115 | 0.112 | 0.122 | 0.116 |
N—number of individuals in each sample; color graduation: minimum (crimson) to maximum (dark green) values.
Figure 2Proportional occurrence of the different 5S-IGS sequence classes (sequence abundance ≥5) in the investigated samples.
Figure 3Neighbor-Net splits graph generated with the 5S-IGS sequences filtered for abundance (≥25) and length (≥280 bp) in all investigated species (a), and all samples belonging to the ‘V. tricolor species complex’ (b).
Figure 4Unrooted maximum likelihood phylograms of the 5S-IGS sequences, filtered for abundance (≥25) and length (≥280 bp), in each sample; sequence class composition and the chromosome number of species/samples are reported.
Figure 5Neighbor-Net splits graph of the 989 5S-IGS sequences filtered for abundance (≥25) and length (≥280 bp) in the investigated dataset. Identified sequence clusters are numbered 1 to 4.
Figure 6BEAST phylogenetic dendrogram of the 989 5S-IGS filtered for abundance (≥25) and length (≥280 bp) in the investigated dataset. Nodes Posterior Probabilities are reported. Major deep clades are evidenced in red and blue.
Investigated dataset.
| Id | Origin | Sampling Site | Taxon | Performed Analysis | |
|---|---|---|---|---|---|
| Plastid DNA | Nuclear rDNA | ||||
| Vt-1 | Switzerland | Novaggio, Lugano | * | ||
| Vt-2 | Germany | Kreis Bad Neustadt/Saale, Bayern | * | * | |
| Vt-3 | Italy | Casalvieri, Frosinone | * | ||
| Va-1 | Italy | Aquilonia, Avellino | * | * | |
| Va-2 | Italy | Roaschia, Cuneo | * | ||
| Vk-1 | Italy | Mt Navegna, Rieti | * | * | |
| Vk-2 | Italy | Bassano Scalo, Orte, Viterbo | * | * | |
| Vh-1 | Italy | Le Vigne, Ofena, L’Aquila | * | * | |
| Vh-2 | Italy | Mt Palanzana, Viterbo | * | * | |
| Vh-3 | Italy | Marchionato, Vetralla, Viterbo | * | * | |
| Va-3 | Italy | Acque Albule, Tivoli, Roma | * | * | |
| Va-4 | Italy | Bagnaccio, Viterbo | * | * | |
| Va-6 | Italy | Basovizza, Trieste | * | ||
| Vh-4 | Italy | Vernole, Acquarica, Lecce | * | * | |
| Va-7 | Italy | Stacchini, Tivoli, Roma | * | * | |
| Va-25 | France | Plateau de Guicule, Le Lavandou | * | ||
| Vh-5 | Italy | Rugoro Grosso, Biancavilla, Catania | * | * | |
| Vh-6 | Italy | Cannarozzo, Piazza Armerina, Enna | * | * | |
| Vh-7 | Italy | Pineta di Biancavilla, Catania | * | * | |
| Vh-8 | Greece | Mt Imittos, Attiki | * | * | |
| Vk-5 | Greece | Mt Pendelikon, Attiki | * | * | |
| Vk-6 | France | Clermont-L’Hérault | * | ||
| Vk-7 | Spain | La Palomera, Córdoba | * | * | |
| Vk-8 | Spain | Los Villares/CO-3408, Córdoba | * | ||
| Vk-9 | Croatia | Šušanj Cesarički, Velebit | * | ||
| Va-26 | Croatia | Radoboj, Hrvatsko Zagorje | * | ||
| Va-8 | Italy | Barrea, l’Aquila | * | * | |
| Va-9 | Italy | San Gregorio da Sassola, Roma | * | * | |
| Va-10 | Italy | Mt Cetona, Siena | * | * | |
| Va-11 | Croatia | Zapadni kolodvor, Zagreb | * | ||
| Va-12 | Croatia | Kozjak, Malačka, Dalmacija | * | ||
| Vt-4 | Italy | Firenzuola, Firenze | * | ||
| Vt-5 | Czec Republic | Ketkovice, Brno-Venkov, Moravia | * | ||
| Vt-6 | Czec Republic | Pavlov, Břeclav, Moravia | * | ||
| Va-16 | Czec Republic | Pavlov, Břeclav, Moravia | * | ||
| Va-27 | Czec Republic | Pavlov, Břeclav, Moravia | * | ||
| Va-28 | Slovacia | Nitra-Zobor, Nitra | * | ||
| Va-18 | Czec Republic | Ráby, distr. Pardubice, Bohemia | * | ||
| Vt-8 | Bosnia–Herzeg. | Planina Dinara, Badanj | * | ||
| Va-20 | Croatia | Gornje Sitno, Mosor, Dalmacija | * | ||
| Va-21 | France | Ludesse, Haute-Loire | * | ||
| Vt-9 | France | Llo, Pyrénées-Orientales | * | * | |
| Vt-10 | France | Beuil, Alpes-Maritimes | * | ||
| Vt-12 | France | La Motte-en-Champsaur, Alpes-Maritimes | * | ||
| Va-23 | France | Saint-Christophe-en-Oisans, Isère | * | ||
| Vt-13 | Italy | Rionero in Vulture, Potenza | * | ||
| Vt-14 | Italy | Chiavari, Genova | * | ||
| Vt-15 | Italy | Vinadio, Cuneo | * | ||
| Vt-16 | Italy | Cortina D’Ampezzo, Belluno | * | ||
| Vt-17 | Bulgaria | Beli Iskar, Rila Mountain | * | * | |
| Vt-18 | Poland | Płociczno, distr. Gmina Bakałarzewo | * | * | |
| Va-24 | Poland | Nadleśnictwo Kędzierzyn | * | ||
| Vk-13 | Italy | Palazzolo, Vasanello, Viterbo | * | ||
| Ve | Italy | Poggio Mutti, Montieri, Grosseto | * | * | |
| Vg | Italy | Selva Rotonda, Cittareale, Rieti | * | * | |
| Vn | Italy | Accadia, Foggia | * | ||
| Vf | Italy | Casalattico, Frosinone | * | ||
| Vae | Albania | Mat River, Klos | * | * | |
| Vr | Italy | Castel Morrone, Caserta | * | ||
* = analyzed samples.